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Water Quality Trading in the Lower Delaware River Basin: A ...

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Figure 3-1. Dra<strong>in</strong>age area and po<strong>in</strong>t source density of watersheds with operat<strong>in</strong>g trad<strong>in</strong>g<br />

systems and TMDL’s that have been developed <strong>in</strong> <strong>the</strong> <strong>Lower</strong> <strong>Delaware</strong> <strong>River</strong> region.<br />

Km 2 /permit<br />

100000<br />

Km 2<br />

10000<br />

1000<br />

100<br />

10<br />

1<br />

0.1<br />

10000<br />

1000<br />

100<br />

10<br />

1<br />

Dra<strong>in</strong>age Area, km 2<br />

US Operat<strong>in</strong>g<br />

<strong>Trad<strong>in</strong>g</strong> Systems<br />

Po<strong>in</strong>t Source Density; Km 2 /permit<br />

US Operat<strong>in</strong>g<br />

<strong>Trad<strong>in</strong>g</strong> Systems<br />

Reduction allocation strategies<br />

Median = 2163<br />

Mean = 8159<br />

N = 14<br />

Median = 41<br />

Mean = 288<br />

N = 71<br />

Mean = 276<br />

N = 12<br />

Median = 190<br />

Median = 12<br />

Mean = 35<br />

N = 32<br />

<strong>Lower</strong> <strong>Delaware</strong><br />

TMDL's<br />

<strong>Lower</strong> <strong>Delaware</strong><br />

<strong>River</strong><strong>in</strong>e TMDL's<br />

On average, <strong>the</strong> TMDL’s <strong>in</strong> <strong>the</strong> <strong>Lower</strong> <strong>Delaware</strong> <strong>River</strong> Bas<strong>in</strong> <strong>in</strong>dicate that a 58%<br />

reduction <strong>in</strong> <strong>the</strong> current <strong>in</strong>put of pollutants is needed to achieve water quality goals<br />

(Figure 3-2). How <strong>the</strong>se reductions are distributed between polluters is critical to <strong>the</strong><br />

achiev<strong>in</strong>g water quality goals <strong>in</strong> an equitable, legally defensible, and economically<br />

efficient manner. Unfortunately, far less than half of <strong>the</strong> 130 regional TMDL’s reviewed<br />

<strong>in</strong> this study explicitly stated how <strong>the</strong> reductions are distributed among dischargers. Less<br />

that 10% of <strong>the</strong> TMDL’s describe <strong>the</strong> details of <strong>the</strong> allocation strategy used to distribute<br />

<strong>the</strong> reductions.<br />

For <strong>the</strong> TMDL’s that do state how <strong>the</strong> reductions are allocated between<br />

dischargers, a size based equal marg<strong>in</strong>al percent removal (EMPR) allocation strategy is<br />

<strong>the</strong> most commonly used method. In this strategy, all dischargers modeled <strong>in</strong> <strong>the</strong> TMDL<br />

are reduced by equal percentages and <strong>the</strong> water quality model is run <strong>in</strong> a reiterative<br />

fashion until <strong>the</strong> WQS are met. Thus <strong>the</strong> marg<strong>in</strong>al rate of removal for all affected<br />

dischargers is <strong>the</strong> same but <strong>the</strong> absolute quantity removed depends on <strong>the</strong> size of <strong>the</strong><br />

discharge. Site specific allocations of NPS reductions are not implicitly considered <strong>in</strong> <strong>the</strong><br />

50

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